JPH04222284A - Method for recycling and pulping waste heat-sensitive recording paper - Google Patents

Method for recycling and pulping waste heat-sensitive recording paper

Info

Publication number
JPH04222284A
JPH04222284A JP2405620A JP40562090A JPH04222284A JP H04222284 A JPH04222284 A JP H04222284A JP 2405620 A JP2405620 A JP 2405620A JP 40562090 A JP40562090 A JP 40562090A JP H04222284 A JPH04222284 A JP H04222284A
Authority
JP
Japan
Prior art keywords
pulp
paper
sensitive recording
concentration
heat
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2405620A
Other languages
Japanese (ja)
Inventor
Masaru Tsuji
辻 勝
Osamu Kitao
修 北尾
Koichi Kawai
河合 晃一
Kazuo Iketani
池谷 一雄
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
TOKAI PULP KK
Kanzaki Paper Manufacturing Co Ltd
Original Assignee
TOKAI PULP KK
Kanzaki Paper Manufacturing Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by TOKAI PULP KK, Kanzaki Paper Manufacturing Co Ltd filed Critical TOKAI PULP KK
Priority to JP2405620A priority Critical patent/JPH04222284A/en
Publication of JPH04222284A publication Critical patent/JPH04222284A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/64Paper recycling

Abstract

PURPOSE:To provide a method for obtaining recycled pulp, having high whiteness and excellent in quality by efficiently separating a heat-sensitive recording material from waste heat-sensitive recording paper. CONSTITUTION:In a method for recycling and pulping waste heat-sensitive paper and obtaining recycled pulp from therefrom, the NaOH concentration based on the waste paper is 1.0-10wt.% and a defoaming agent is added into an aqueous solution of NaOH. The aqueous solution of the NaOH is kept at 30-60 deg.C temperature. In this state, waste paper pulp concentration is regulated to >=10wt.% to carry out alkali disintegration of the waste paper. A deinking agent and a peroxide are added to the resultant disintegrated waste paper pulp and the obtained pulp is subjected to mechanical stirring treatment at a high concentration.

Description

【発明の詳細な説明】 【0001】 【産業上の利用分野】本発明は、感熱記録紙古紙(損紙
も含む)を用いて再生パルプを得る方法に関し、特に感
熱記録材料をパルプ繊維から効率よく分離し、白色度の
高い再生パルプを得る感熱記録紙古紙のパルプ化法に関
する。 【0002】 【従来の技術】一般に、パルプ繊維からなる原紙上に微
粒子状の塩基性無色染料、呈色剤、増感剤、顔料、バイ
ンダー及び助剤等から成る感熱記録材料層を設けた感熱
記録紙は広く知られている。この感熱記録紙に熱を加え
ると、その部分の増感剤及び呈色剤が融解し、塩基性無
色染料と接触して発色画像が得られる。感熱記録紙の発
色画像は、一般に耐水性、耐油性、耐可塑剤性等に劣っ
ている。この為、例えば発色画像に水、油あるいはプラ
スチックフィルムに含まれる可塑剤等が接触すると、画
像濃度が著しく低下し、又、取扱い中に感熱記録層を手
で触れると指紋状のカブリ発色を生じる等の欠点を有し
ている。 【0003】上記の如き問題を解消するために、例えば
感熱記録層上又は裏面に水性エマルジョン塗布層、水溶
性高分子化合物塗布層、硬化剤で硬化させた水溶性高分
子層等の保護層を設けた感熱記録紙がラベル等の分野で
広く用いられるようになってきた。一方、近年感熱記録
紙の生産、需要の増大に伴い、そこから派生する感熱記
録紙の古紙処理が環境対策面よりクローズアップされつ
つあり、その一環として感熱記録紙古紙の再生利用法の
開発が新たな課題となりつつある。 【0004】従来より、新聞古紙や印刷コート紙古紙の
再生パルプ化は行われており、一般的には古紙を離解し
てパルプ懸濁液を得る離解工程、パルプ懸濁液中の異物
を分離する粗選、精選工程、印刷インキを分離する脱墨
工程、色を白くする漂白工程等を経て再生パルプ化が行
われている。 【0005】例えば、特公昭50−29042 号には
、印刷コート紙の離解及び粗選工程、脱水工程、漂白工
程、インキの分離工程からなる古紙再生方法が提案され
ており、特開昭50−6802号には、界面活性剤を含
むアルカリ液を使用して、離解処理する方法等が示され
ている。又、特開昭63−135585号には、感熱記
録古紙を界面活性剤を含有するアルカリ性水溶液中で離
解処理した後、中和する工程、離解された古紙スラリ−
を浮遊選別する工程、脱水絞り機で濃縮する工程、高速
離解機で離解する工程を経て再生する方法が提案されて
いる。しかし、これらの方法を耐水性、耐油性、耐可塑
剤性等のある保護層を有する感熱記録紙を含む感熱記録
紙古紙に適用すると、保護層の未離解片が残存し、この
パルプを使用して、抄紙すると抄紙機の乾燥工程で該感
熱記録材料が発色して得られる紙の白色度が低下する。 また、特開平2 −133688号には、呈色剤を除去
し、繊維中に残存する呈色剤の重量を残存する塩基性染
料の重量より少なくした後に、ニーディング処理をする
方法が提案されている。しかしながら、この方法を保護
層を有する感熱記録紙の古紙に適用しても、保護層の離
解が十分にできないまま次のニーデイング工程に行くた
め、この場合もニーディング工程で塩基性染料が発色し
てしまい、高白色度のパルプを得ることができない。上
記の如き事情から、感熱記録紙古紙の再生パルプ化は敬
遠され、産業廃棄物となっているのが現状である。 【0006】 【発明が解決しようとする課題】本発明は、感熱記録紙
古紙(損紙も含む)を用いて、再生パルプを得る方法に
関するものであり、特に保護層を含む感熱記録材料層を
パルプ繊維から効率よく分離することによって、熱によ
って発色することがなく、且つ白色度の高い再生パルプ
を得るためのパルプ化法を提供するものである。 【0007】 【課題を解決するための手段】本発明は、感熱記録紙の
古紙をNaOH水溶液中で離解して離解パルプとした後
、脱墨剤及び過酸化物を添加し、次いで該離解パルプを
高濃度機械的攪拌処理する方法において、下記条件(a
) 〜(d) を満足するように処理することを特徴と
する感熱記録紙古紙の再生パルプ化法である。 (a) ; NaOH水溶液が消泡剤を含む(b) ;
 NaOHの濃度が古紙パルプに対し、1〜10重量% (c) ; 離解時のNaOH水溶液の温度が30〜6
0℃(d) ; 離解時の古紙パルプの濃度が10重量
%以上     【0008】 【作用】本発明で対象とする感熱記録紙古紙としては、
例えばファクシミリ、プリンター、ラベル等で商業用、
事務用、家庭用等、広範囲の用途に使用されている感熱
記録紙、或いはそれらの感熱記録紙を製造する過程で発
生する半製品や損紙等が含まれる。 【0009】前述したように、本発明の古紙処理方法で
は、感熱記録紙古紙を先ずパルパー等の離解機を使用し
て、特定条件下でのNa0H水溶液で離解してパルプ懸
濁液を作る。この場合、Na0H溶液を用いるのは、感
熱記録材料層の離解促進及び感熱記録材料層中の呈色剤
を水可溶性にするためである。 【0010】なお、呈色剤としては、一般的にはフェノ
ール化合物、芳香族カルボン酸等の有機酸が使用されて
いるが、これらはNa0H溶液でNa塩となり、水に可
溶化する形となり感熱記録材料層から溶出される。一方
、トリアリルメタン系、フェニルメタン系、チアジン系
、フルオラン系等の塩基性染料はNa塩となった呈色剤
とは反応して発色することはない。 【0011】ここに、Na0Hの感熱記録紙古紙との作
用を円滑に行わしめるには、Na0Hを該古紙に対して
1.0 〜10重量%、好ましくは1.0 〜5重量%
の範囲で添加する必要がある。因みに、Na0Hの添加
量が10重量%を越えるとアルカリ加水分解が起こり、
得られる再生パルプの強度が低下する。一方、1.0 
重量%未満の場合には、感熱記録材料層中の呈色剤が充
分にNa塩へ変換されない。また、離解する際のNa0
H水溶液の温度が60℃を越えると、感熱記録材料層中
の呈色剤がNa塩になる前に、感熱記録材料層に熱がか
かり発色してパルプ繊維に吸着し、得られる再生パルプ
の白色度が低下するので好ましくない。一方、30℃未
満の場合には、感熱記録材料層に含まれるバインダーや
保護層中の樹脂が硬くなり、原紙層は離解されるものの
、感熱記録材料層及び保護層の離解が不十分となる。結
果として、感熱記録材料層からの呈色剤のNa塩化が不
十分のまま、次のニーディング工程に行くため、ニーデ
ィング工程で塩基性染料が発色する。また、離解時間も
長く掛り経済上問題である。従って、本発明では離解時
のアルカリ水溶液の液温度を30〜60℃に特定するも
のである。 【0012】本発明では、感熱記録紙古紙のアルカリ水
溶性液による離解を効率的に実施するために、パルプ濃
度を10重量%以上にする必要がある。即ち、パルプ濃
度を10重量%以上に特定することによって、必然的に
溶液中のNa0H濃度が高くなり、原紙の離解が促進さ
れるのみならず、パルプ繊維と感熱記録材料層との機械
的な摩擦により感熱記録材料層の離解も促進される。因
みに、10重量%以下であると溶液中のNa0H濃度も
低くなり、それだけ離解が悪くなる。結果として、離解
工程の後工程で古紙パルプ中に含まれる異物を取り除く
ためにスクリーン処理を行うが、このとき未離解のパル
プ繊維が除去され、得られる再生パルプの収率が低下す
る。 なお、パルプ濃度が40重量%を越えると攪拌、混合が
難しくなり離解ができない。従って、離解時のパルプ濃
度は10〜40重量%に特定されるものである。 【0013】一般的には、感熱記録塗料は感熱記録材料
の塗料調製段階で記録感度を向上させるために各分散液
中の材料を数μ以下に微粒子化する必要がある。この微
粒子化を円滑に行うために、分散時或いは湿式粉砕時に
界面活性剤や保護コロイド剤等の助剤を使用することが
多い。また、PVA、ラテックス等のバインダーも使用
されるために、これらを含む感熱記録紙古紙の離解(攪
拌)工程では多量の空気を抱き込み、得られる懸濁液中
に泡が多量に存在することになる。この泡が脱水濃縮や
洗浄等の工程での洗浄効率を著しく低下させることにな
り、パルプ繊維表面に感熱記録材料を残す原因となる。 又、脱水濃縮後の排水は、凝集浮上、凝集沈澱等の排水
処理を施し回収水として使用されるが、処理工程で泡が
発生し、キャリーオーバーを起こす等して排水の処理効
率を低下させる原因となる。本発明では、これらの泡を
抑制するために、離解工程で消泡剤を添加する。消泡剤
の添加によって感熱記録材料層をパルプ繊維から効率よ
く分離し、白色度が高く、且つ品質の安定した再生パル
プを効率良く得ることができる。 【0014】なお、消泡剤としては、具体的にはポリグ
リコール・脂肪酸混合物、燐酸エステル、シリコンエマ
ルジョン系、非イオン性脂肪酸混合物、ポリグリコール
エステル、アルコール系、植物油系、脂肪酸エステル、
松根油エマルジョン、硫酸エステル系、金属石鹸系等が
挙げられる。その種類に付いては特に限定されるもので
はなく、使用する古紙の種類や液温等によって、適宜選
択すればよい。消泡剤の添加量は古紙に対して、一般的
には0.0001〜0.1 重量%程度の範囲で添加す
れば良い。 また、消泡剤を離解工程で添加しても不十分な場合には
、洗浄工程や脱水濃縮に入る直前で添加することも勿論
可能である。 【0015】本発明において、使用される離解機として
は特に限定されるものではないが、推奨される好ましい
離解機はヘリカルローターを有する高濃度パルパーが望
ましい。感熱記録紙古紙の離解の場合、古紙中に感圧接
着剤やプラスチック等( 以下、単に異物という) が
含まれている場合には、当然離解後の懸濁液中に異物が
混入しているので、これら異物を分離する必要がある。 その分離のために、スクリーン工程が設けられる。なお
、この古紙を離解する場合には、これらの異物が攪拌機
等によって、機械的作用を過度に受けると小さく砕かれ
、スクリーン工程でスクリーンの目穴から抜け出てしま
い分離効果を悪くする恐れがあるだけでなく、再生パル
プ中に異物が含まれることになる。その結果として、抄
紙工程で異物がワイヤーの目を塞いだり、プレスロール
や毛布を汚染したりして、紙切れを誘発し、生産性を著
しく低下させる原因になる。また、紙面上に斑点を形成
する等して品質面にも悪影響を及ぼすことになる。 【0016】従って、離解程度としては該異物がスクリ
ーンの目穴よりは細かくならないように配慮することが
重要である。通常、スクリーン工程の設置場所は離解工
程の後、機械的攪拌工程の後、泡沫浮上分離工程の後に
1箇所又は2箇所以上に亘って設置される。スクリーン
の設置箇所等については、特に限定するものでなく、異
物の量、種類等により適宜選択すればよい。 【0017】かくして得られた感熱記録紙古紙の懸濁液
を脱水濃縮してパルプ濃度を20重量%以上にする。こ
の脱水濃縮過程で、Na塩となり水溶化した呈色剤や顔
料等の感熱記録材料の大部分がパルプ繊維と分離除去さ
れる。脱水濃縮工程には、公知の脱水濃縮機が利用でき
るが、特に傾斜型のスクリュウシックナーとスクリュウ
プレスとの組合せが、本発明の所望の効果を得る上で好
ましく使用される。 【0018】次に、パルプ濃度を20重量%以上に調整
した古紙パルプ懸濁液を機械的に強攪拌して粒状の感熱
記録層を微小粒子に分散を行う必要がある。耐水性、耐
油性、耐可塑剤性等の特性を有する保護層を設けた感熱
記録紙古紙は、通常の離解機では、原紙層は容易に離解
されるが、感熱記録層は粒状粒子として残り、懸濁液中
に混在する。この粒状粒子の中には感熱記録材料が存在
し、容易に取り除くことができない。このために、懸濁
液のパルプ濃度を20重量%以上に調整して、機械的攪
拌を行うとこの粒状粒子を微小粒子に分散することが可
能となる。因みに、パルプ濃度が20重量%未満の場合
には、その分散効率が悪く粒状粒子が懸濁液中に残る。 この粒状粒子中には感熱記録材料が含有されている。ま
た、この粒状粒子は後工程の泡沫浮上分離でも取り除く
ことが出来ない。尚、パルプ濃度が40重量%を越える
と、機械的な攪拌混合が難しくなるので、機械的攪拌を
行うときのパルプ懸濁液のパルプ濃度は20〜40重量
%の範囲で調節する必要がある。 【0019】本発明における機械的攪拌の方法は圧縮作
用が付随する機械的な強攪拌を指しており、例えば、一
般的に使用されているニーダー、二軸ミキサー、ディス
パーザー等の攪拌機を適宜使用することができ、特に限
定されるものではない。なお、この機械的攪拌処理の場
合にも、離解工程の時と同様に、未だ感熱記録材料が残
存しているので、この感熱記録材料の発色を抑制するた
めに、処理時の温度を60℃以下に維持することが好ま
しい。 【0020】機械的に高濃度攪拌処理後、パルプ濃度を
2〜5重量%に希釈して更に機械的攪拌を行う。これは
、前工程でパルプ濃度が20重量%以上で機械的強攪拌
を行っているために、パルプ繊維同士の絡み合いにより
繊維が毛球状となっている。その絡み合った毛球の中に
感熱記録材料が一部取り込まれている。この毛球状のパ
ルプは通常のチェストに装備されているアジテーターで
は解きほぐせない。この毛球状のパルプ懸濁液の状態で
次工程の泡沫浮上分離を行っても感熱記録材料を完全に
除去することが出来ず、得られた再生パルプの白色度は
低下する。そのために、2〜5重量%のパルプ濃度にし
て機械的攪拌を行ないパルプ繊維の絡み合いをときほぐ
し、単繊維化する。このときの機械的攪拌に用いられる
設備は、通常使用されている高速離解機やリファイナー
等が挙げられ、特に、限定するものではない。 【0021】さらに、上記の如く低濃度下で機械的攪拌
処理を受けた古紙パルプ懸濁液に脱墨剤を添加した後、
パルプ濃度を0.3 〜1.5 重量%に調節して空気
を吹き込み、泡沫浮上分離を行い、未だパルプ懸濁中に
残存している感熱記録材料を泡と共に取り除く。このと
きに使用される脱墨剤は、一般に使用されている新聞古
紙用の脱墨剤が使用でき、特に、脂肪酸石鹸、脂肪酸及
び油脂系のエチレンオキシド・プロピレンオキシドの付
加物からなる脱墨剤は、泡の表面に感熱記録材料を良く
付着させる傾向が強く、泡沫浮上分離工程で感熱記録材
料を泡と共に浮上分離させるのに優れた作用効果を発揮
するので、好ましい脱墨剤である。脱墨剤の添加量は、
泡立ちの状況をみて適宜調整すればよく、通常、乾燥パ
ルプに対して0.01〜1.0 重量%の範囲で添加さ
れる。なお、脱墨剤の添加場所は泡沫浮上分離時でも良
いが、好ましくは機械的攪拌工程の前、特に、パルプ濃
度が20重量%以上の機械的攪拌工程で添加すると脱墨
剤がパルプ懸濁液中に効率良く分散されるので、望まし
い実施態様である。さらに、機械的攪拌後1時間以上放
置した方が脱墨剤と感熱記録記録材料との吸着が良くな
り、感熱記録材料のパルプからの分離効果がより改善さ
れる。本発明で使用する泡沫浮上分離装置は、特に限定
するものでなく、従来からあるフローテーター等を適宜
使用することができる。 【0022】また、本発明では、このようにして得られ
た再生パルプの白色度をより高めるために、高濃度機械
的攪拌工程に入る前にパルプ懸濁液に過酸化物を添加し
、極く微量に残存している感熱記録材料を酸化漂白する
。過酸化物としては、例えば過酸化水素、過酸化ソーダ
、過炭酸ソーダ等が挙げられ、特に、限定するものでな
い。過酸化物の添加量は対パルプ当たり0.2 〜5重
量%添加すれば良く、パルプの白色度を測定しながら、
適宜選択すれば良い。なお、過酸化物の安定剤として、
通常の過酸化物漂白で使用される、例えばケイ酸ナトリ
ウム、キレート剤、水酸化ナトリウム、硫酸マグネシウ
ム等から選ばれる1種或いは2種以上が併用添加される
。 【0023】パルプ中に重量異物がある場合には、クリ
ーナー処理をするのが望ましい。一方、軽量異物がある
場合には、ジロクリーン等の軽量異物分離工程を設ける
と良い。更に、残漂白剤や感熱記録材料の分解物、残存
脱墨剤等を取り除くための洗浄工程を設けると良い。洗
浄方法としては置換洗浄、希釈脱水洗浄、プレス洗浄等
が適宜使用される。 【0024】また、紙の強度を上げるために、パルプ濃
度を3〜4重量%にして、叩解することも可能であり、
叩解程度は紙の品質目標に合わせて適宜行えば良い。か
くして得られた白い再生パルプは抄紙工程で発色するこ
となく、且つ、ピンホールや斑点状の微小異物も極めて
少なく、有効に抄紙原料として使用できる。 【0025】 【実施例】以下に、実施例を挙げて本発明をより具体的
に説明するが、勿論これらに限定するものでない。なお
、例中の%は「重量%」を示す。 【0026】実施例1〔離解工程〕パルパー(相川鉄工
製;高濃度パルパー)に保護層を有する感熱記録紙の古
紙と、該古紙に対しNa0Hを1.5 %添加し、さら
に消泡剤(ノプコ1407−K/サンノプコ社製)を乾
燥固形分に対して0.01%添加して、パルプ濃度が1
5%となるように温水(55℃)を仕込み、30分間離
解した。 【0027】〔スクリーン工程〕上記で得られたパルプ
懸濁液をパルプ濃度が3.5 %になるように希釈して
、スリット幅0.2 mmのスクリーン(ファインスク
リーン/相川鉄工製)を用いて処理した。 【0028】〔機械的攪拌工程〕次に、アクセプトをパ
ルプ濃度が28%になるように脱水濃縮機(傾斜エキス
トラクター、スクリュウプレス/相川鉄工製)を用いて
脱水濃縮した。この脱水濃縮したパルプの乾燥固形分に
対して過酸化水素2%、ケイ酸ナトリウム2%、脱墨剤
(DI−600 R/花王製)0.3 %をそれぞれ添
加し、機械的強攪拌(ディスパーザー/相川鉄工製)処
理を行った。この機械的攪拌処理されたパルプを50℃
で100 分間放置(熟成)した後、このパルプを取り
出してパルプ濃度が4%になるように希釈した後、高速
離解機(トップファイナー/相川鉄工製)でパルプを分
散した。 【0029】〔泡沫浮上分離工程〕上記の分散パルプ懸
濁液を、更に、パルプ濃度が1.0 %になるように希
釈し、空気を導入しながら攪拌を行い、泡沫浮上分離装
置(バーチカルフロテーター/相川鉄工製)にかけて浮
上分離処理を行った。 【0030】〔後処理工程〕続けて、上記浮上分離処理
を終えたパルプ懸濁液を重量異物除去用のクリナー、及
び軽量異物除去用装置(ジロクリーン/相川鉄工製)に
通して処理を行った後、脱水濃縮した。 【0031】〔結果〕かくして得られた再生パルプをT
APPI STD T218に準じて手抄シートに仕上
げ、風乾後白色度をエルレホ白色度計(エルレホ200
0)を用いて測定した。また、張力は60g/m2 の
手抄シートを調製し、JISp8113に準じて測定し
た。このとき得られた白色度及び張力は、それぞれ83
%、3.7 Kgであった。別に、この再生パルプとバ
ージンパルプ(50:50) とを配合して抄紙したが
、紙のドライヤー(加熱)での発色はなかった。なお、
得られた結果を表1に示した。 【0032】実施例2〔離解工程〕パルパー(高濃度パ
ルパー/相川鉄工製)に保護層のある感熱記録紙の古紙
、及び該古紙に対してNa0Hを5%添加し、さらに消
泡剤(ノプコDFー122 /サンノプコ社製)を乾燥
固形分に対して0.03%添加して、パルプ濃度が20
%となるように温水(30℃)を仕込み、40分間離解
した。 【0033】〔スクリーン工程〕上記のパルプ懸濁液を
パルプ濃度が3.5 %になるように希釈調製して、ス
リット幅0.2 mmのスクリーン(ファインスクリー
ン/相川鉄工製)を用いて処理した。 【0034】〔機械的攪拌工程〕次に、アクセプトをパ
ルプ濃度が30%になるように脱水濃縮機(傾斜エキス
トラクター、スクリュウプレス/相川鉄工製)をもちい
て脱水濃縮した。この脱水濃縮したパルプの乾燥固形分
に対して過酸化水素5%、ケイ酸ナトリウム3%、脱墨
剤(DI−610 /花王製)0.3 %をそれぞれ添
加し、機械的攪拌(ディスパーザー/相川鉄工製)処理
を行った。 この機械的攪拌処理されたパルプを50℃で100 分
間放置した後、このパルプを取り出してパルプ濃度が4
%になるように希釈して高速離解機(トップファイナー
/相川鉄工製)でパルプを分散した。 【0035】〔泡沫浮上分離工程〕上記の分散パルプ懸
濁液を、更に、パルプ濃度が1.0 %になるように希
釈し、空気を導入しながら攪拌を行い、泡沫浮上分離装
置(バーチカルフロテーター/相川鉄工製)にかけて浮
上分離処理を行った。 【0036】〔後処理工程〕続けて、上記浮上分離処理
を終えたパルプ懸濁液を重量異物除去用のクリナー、及
び軽量異物除去用装置(ジロクリーン/相川鉄工製)に
通して処理を行った後、脱水濃縮した。 【0037】〔結果〕かくして得られた再生パルプを実
施例1と同様に処理して、手抄シートの白色度及び張力
を測定したところ、それぞれ84%、3.6 Kgであ
った。得られた結果を表1に示した。なお、同パルプを
実施例1と同様にして抄紙したが、紙のドライヤーでの
発色はなかった。 【0038】実施例3〔離解工程〕パルパー(高濃度パ
ルパー/相川鉄工製)に保護層を有する感熱記録紙の古
紙と、該古紙に対してNa0Hを1.5 %添加し、さ
らに消泡剤(フォームクリーンMー48/伯東化学社製
)を乾燥固形分に対して0.03%添加して、パルプ濃
度が25%となるように温水(45℃)を仕込み、60
分間離解した。 【0039】〔粗撰スクリーン工程〕上記のパルプ懸濁
液をパルプ濃度が3.5 %になるように希釈調製して
、スリット幅0.3 mmのスクリーン(ファインスク
リーン/相川鉄工製)を用いて処理した。 【0040】〔機械的攪拌工程〕次に、アクセプトをパ
ルプ濃度が30%になるように脱水濃縮機(傾斜エキス
トラクター、スクリュウプレス/相川鉄工製)をもちい
て脱水濃縮した。この脱水濃縮したパルプの乾燥固形分
に対して過酸化水素0.5 %、ケイ酸ナトリウム1%
、脱墨剤(DI−610 /花王製)0.3 %をそれ
ぞれ添加し、機械的攪拌(ディスパーザー/相川鉄工製
)処理を行った。この機械的攪拌処理されたパルプを5
0℃で100 分間放置した後、このパルプを取り出し
てパルプ濃度が4%になるように希釈して高速離解機(
相川鉄工製;トップファイナー)でパルプを分散した。 【0041】〔泡沫浮上分離工程〕上記の分散パルプ懸
濁液を、更にパルプ濃度が0.7 %になるように希釈
し、空気を導入しながら攪拌し、泡沫浮上分離装置(バ
ーチカルフロテーター/相川鉄工製)にかけて浮上分離
処理を行った。 【0042】〔スクリーン工程〕上記のパルプ懸濁液を
スリット幅0.2 mmのスクリーン(ファインスクリ
ーン/相川鉄工製)を用いて処理した。 【0043】〔後処理工程〕続けて、上記浮上分離処理
を終えたパルプ懸濁液を重量異物除去用のクリナー、及
び軽量異物除去用装置(ジロクリーン/相川鉄工製)に
通して処理を行った後、脱水濃縮した。 【0044】〔結果〕かくして得られた再生パルプを実
施例1と同様に処理して、手抄シートの白色度及び張力
を測定したところ、それぞれ81%、3.8 Kgであ
った。得られた結果を表1に示した。なお、同パルプを
実施例1と同様にして抄紙したが、紙のドライヤーでの
発色はなかった。 【0045】実施例4〔離解工程〕パルパー(高濃度パ
ルパー/相川鉄工製)に保護層を有する感熱記録紙の古
紙と、該古紙に対してNa0Hを2%添加し、さらに消
泡剤(ノプコ1407−K/サンノプコ社製)を乾燥固
形分に対して0.01%添加して、パルプ濃度が15%
となるように温水(55℃)を仕込み、30分間離解し
た。 【0046】〔粗撰スクリーン工程〕上記のパルプ懸濁
液をパルプ濃度が3.5 %になるように希釈調製して
、スリット幅0.25mmのスクリーン(ファインスク
リーン/相川鉄工製)を用いて処理した。 【0047】〔機械的攪拌工程〕次に、アクセプトをパ
ルプ濃度が25%になるように脱水濃縮機(傾斜エキス
トラクター、スクリュウプレス/相川鉄工製)を用いて
脱水濃縮した。この脱水濃縮したパルプの乾燥固形分に
対して過酸化水素1%、ケイ酸ナトリウム1%、脱墨剤
(DI−610 /花王製)0.3 %をそれぞれ添加
し、機械的攪拌(ディスパーザー/相川鉄工製)処理を
行った。 この機械的攪拌処理されたパルプを50℃で50分間放
置した後、このパルプを取り出してパルプ濃度が4%に
なるように希釈して高速離解機(トップファイナー/相
川鉄工製)でパルプを分散した。 【0048】〔スクリーン工程〕上記で得られたパルプ
懸濁液を、更に、パルプ濃度が1.0 %になるように
希釈調製して、スリット幅0.2 mmのスクリーン(
ファインスクリーン/相川鉄工製)を用いて処理した。 【0049】〔泡沫浮上分離工程〕上記の分散パルプ懸
濁液に空気を導入しながら攪拌し、泡沫浮上分離装置(
バーチカルフロテーター/相川鉄工製)にかけて浮上分
離処理を行った。 【0050】〔後処理工程〕続けて、上記浮上分離処理
を終えたパルプ懸濁液を重量異物除去用のクリナー、及
び軽量異物除去用装置(ジロクリーン/相川鉄工製)に
通して処理を行った後、脱水濃縮した。 【0051】〔結果〕かくして得られた再生パルプを実
施例1と同様に処理して、手抄シートの白色度及び張力
を測定したところ、それぞれ81%、3.7 Kgであ
った。得られた結果を表1に示した。なお、同パルプを
実施例1と同様にして抄紙したが、紙のドライヤーでの
発色はなかった。 【0052】実施例5〔離解工程〕パルパー(高濃度パ
ルパー/相川鉄工製)に保護層を有する感熱記録紙の古
紙と、該古紙に対してNa0Hを1.25%添加し、さ
らに消泡剤(ノプコ1407−K/サンノプコ社製)を
乾燥固形分に対して0.07%添加して、パルプ濃度が
15%となるように温水(58℃)を仕込み、30分間
離解した。 【0053】〔粗撰スクリーン工程〕上記のパルプ懸濁
液をパルプ濃度が3.5 %になるように希釈調製して
、スリット幅 0.3mmのスクリーン(ダブルセパレ
ーター/相川鉄工製)を用いて処理した。 【0054】〔機械的攪拌工程〕次に、アクセプトをパ
ルプ濃度が33%になるように脱水濃縮機(傾斜エキス
トラクター、スクリュウプレス/相川鉄工製)を用いて
脱水濃縮した。この脱水濃縮したパルプの乾燥固形分に
対して過酸化水素1%、ケイ酸ナトリウム2.5 %、
脱墨剤(DI− 600R/花王製)0.6 %をそれ
ぞれ添加し、機械的攪拌(ディスパーザー/相川鉄工製
)処理を行った。この機械的攪拌処理されたパルプを5
0℃で 120分間放置した後、このパルプを取り出し
てパルプ濃度が4%になるように希釈して高速離解機(
トップファイナー/相川鉄工製)でパルプを分散した。 【0055】〔泡沫浮上分離工程〕上記の分散パルプ懸
濁液を、更にパルプ濃度が1%になるように希釈し、空
気を導入しながら攪拌し、泡沫浮上分離装置(バーチカ
ルフロテーター/相川鉄工製)にかけて浮上分離処理を
行った。 【0056】〔スクリーン工程〕上記パルプ懸濁液の濃
度を1%に希釈調製して、スリット幅0.2 mmのス
クリーン(ファインスクリーン/相川鉄工製)を用いて
精選処理した。 【0057】〔後処理工程〕続けて、上記浮上分離処理
を終えたパルプ懸濁液を重量異物除去用のクリナー、及
び軽量異物除去用装置(ジロクリーン/相川鉄工製)に
通して処理を行った後、脱水濃縮した。 【0058】〔結果〕かくして得られた再生パルプを実
施例1と同様に処理して、手抄シートの白色度及び張力
を測定したところ、それぞれ82%、3.8 Kgであ
った。得られた結果を表1に示した。なお、同パルプを
実施例1と同様にして抄紙したが、紙のドライヤーでの
発色はなかった。 【0059】比較例1 実施例1において、離解工程で使用したNa0Hと消泡
剤の添加を止めた以外は実施例1と同様にして調製、処
理を行って、再生パルプを得た。このときに得られた再
生パルプの手抄シートの張力は 3.8Kgであったが
、エルレホ白色度は60%と実施例1に比較し、かなり
悪く、この再生パルプとバージンパルプ(50:50)
を配合して抄紙した紙はドライヤーで少し発色した。得
られた結果を表1に示した。 【0060】比較例2 実施例1において、離解工程で使用した消泡剤の添加を
止め、温水の温度を70℃に変更した以外は実施例1と
同様にして調製、処理を行って、再生パルプを得た。こ
のときに得られた再生パルプの手抄シートの張力は 3
.7Kgであったが、エルレホ白色度は70%と実施例
1に比較し悪く、この再生パルプとバージンパルプ(5
0:50)を配合して抄紙した紙はドライヤーで少し発
色した。得られた結果を表1に示した。 【0061】比較例3 実施例1において、離解工程で使用した消泡剤の添加を
止め、さらにパルプ濃度を6%に変更した以外は実施例
1と同様にして調製、処理を行って、再生パルプを得た
。このときに得られた再生パルプの手抄シートの張力は
 3.9Kgであったが、エルレホ白色度は73%と実
施例1に比較し悪く、この再生パルプとバージンパルプ
(50:50)を配合して抄紙した紙はドライヤーで少
し発色した。得られた結果を表1に示した。 【0062】比較例4 実施例1において、Na0Hの添加を 1.2%に変更
した以外は実施例1と同様にして調製、処理を行って、
再生パルプを得た。このときに得られた再生パルプのエ
ルレホ白色度は83%と実施例1と同等であるが、手抄
シートの張力が 3.0Kgと低下した。得られた結果
を表1に示した。 【0063】比較例5 実施例1において、離解工程で使用したNa0Hの添加
量を0.5 %、機械的攪拌工程でのパルプ濃度を10
%にそれぞれ変更した以外は実施例1と同様にして調製
、処理を行って、再生パルプを得た。このときに得られ
た再生パルプの手抄シートの張力は 3.7Kgであっ
たが、エルレホ白色度は62%と実施例1に比較し、か
なり悪く、この再生パルプとバージンパルプ(50:5
0)を配合して抄紙した紙はドライヤーで粒状の発色斑
点が出た。得られた結果を表1に示した。 【0064】 【表1】 【0065】 【発明の効果】実施例から明らかなように、保護層を設
けた感熱記録紙の古紙から得られた再生パルプは高白色
度を維持することができ、且つ該古紙再生パルプから得
られる紙シートを加熱しても発色や粒状の発色斑点は認
められなかった。
Detailed Description of the Invention [0001] [Industrial Application Field] The present invention relates to a method for obtaining recycled pulp using heat-sensitive recording paper waste paper (including waste paper), and particularly relates to a method for obtaining recycled pulp from heat-sensitive recording paper from pulp fibers. This invention relates to a method for pulping waste heat-sensitive recording paper to obtain recycled pulp with good separation and high whiteness. [0002] Generally, a thermosensitive recording material layer comprising a basic colorless dye in the form of fine particles, a coloring agent, a sensitizer, a pigment, a binder, an auxiliary agent, etc. is provided on a base paper made of pulp fibers. Recording paper is widely known. When heat is applied to this thermosensitive recording paper, the sensitizer and coloring agent in that area melt and come into contact with the basic colorless dye, producing a colored image. Colored images produced by thermosensitive recording paper are generally inferior in water resistance, oil resistance, plasticizer resistance, and the like. For this reason, for example, if a colored image comes into contact with water, oil, or a plasticizer contained in a plastic film, the image density will drop significantly, and if the heat-sensitive recording layer is touched by hand during handling, fingerprint-like fogging will occur. It has the following drawbacks. In order to solve the above-mentioned problems, for example, a protective layer such as a water-based emulsion coating layer, a water-soluble polymer compound coating layer, a water-soluble polymer layer cured with a curing agent, etc. is applied on the heat-sensitive recording layer or on the back side. Thermal recording paper provided with this method has come to be widely used in fields such as labels. On the other hand, as the production and demand for thermal recording paper has increased in recent years, the treatment of waste thermal recording paper derived from it has been attracting more attention from an environmental perspective. This is becoming a new issue. [0004] Conventionally, recycled pulp from used newspapers and printed coated paper has been carried out, and generally involves a disintegration process in which waste paper is disintegrated to obtain a pulp suspension, and foreign substances in the pulp suspension are separated. Recycled pulp is produced through a rough selection process, a fine selection process, a deinking process to separate the printing ink, and a bleaching process to whiten the color. [0005] For example, Japanese Patent Publication No. 50-29042 proposes a method for recycling used paper, which consists of disintegration and rough selection of printed coated paper, dehydration, bleaching, and ink separation. No. 6802 discloses a method of disintegration treatment using an alkaline solution containing a surfactant. Furthermore, JP-A-63-135585 discloses a process of disintegrating heat-sensitive recording paper in an alkaline aqueous solution containing a surfactant and then neutralizing the disintegrated waste paper slurry.
A method has been proposed in which recycled materials are recycled through a process of flotation sorting, concentrating with a dehydration squeezer, and disintegrating with a high-speed disintegrator. However, when these methods are applied to waste thermal recording paper, including thermal recording paper that has a protective layer with water resistance, oil resistance, plasticizer resistance, etc., undisintegrated pieces of the protective layer remain, making it difficult to use this pulp. When paper is made, the heat-sensitive recording material develops color during the drying process of the paper machine, reducing the whiteness of the resulting paper. Furthermore, JP-A-2-133688 proposes a method in which a kneading treatment is performed after removing a coloring agent and reducing the weight of the coloring agent remaining in the fibers to be less than the weight of the remaining basic dye. ing. However, even when this method is applied to waste heat-sensitive recording paper that has a protective layer, the protective layer is not sufficiently disintegrated before the next kneading process is carried out, so the basic dye develops color in the kneading process. As a result, pulp with high whiteness cannot be obtained. Due to the above-mentioned circumstances, the conversion of waste heat-sensitive recording paper into recycled pulp is avoided, and the paper is currently treated as industrial waste. [0006] The present invention relates to a method for obtaining recycled pulp using waste heat-sensitive recording paper (including waste paper), and particularly relates to a method for obtaining recycled pulp using a heat-sensitive recording material layer including a protective layer. The purpose of the present invention is to provide a pulping method for obtaining recycled pulp that does not develop color due to heat and has a high degree of whiteness by efficiently separating it from pulp fibers. Means for Solving the Problems [0007] The present invention disintegrates waste heat-sensitive recording paper in an aqueous NaOH solution to form a disintegrated pulp, adds a deinking agent and a peroxide, and then disintegrates the disintegrated pulp. In the method of high-concentration mechanical stirring treatment, the following conditions (a
) to (d) This is a method for converting waste heat-sensitive recording paper into recycled pulp, which is characterized by processing it so as to satisfy the following. (a); The NaOH aqueous solution contains an antifoaming agent (b);
The concentration of NaOH is 1 to 10% by weight based on the waste paper pulp (c); The temperature of the NaOH aqueous solution during disintegration is 30 to 6% by weight
0°C (d); The concentration of waste paper pulp at the time of disintegration is 10% by weight or more. [Action] The waste heat-sensitive recording paper targeted by the present invention includes:
For example, for commercial use such as fax machines, printers, labels, etc.
This includes thermal recording paper used for a wide range of purposes such as office and household use, as well as semi-finished products and waste paper generated in the process of manufacturing such thermal recording paper. As described above, in the waste paper processing method of the present invention, waste heat-sensitive recording paper is first disintegrated with an NaOH aqueous solution under specific conditions using a disintegrator such as a pulper to form a pulp suspension. In this case, the reason why the NaOH solution is used is to promote disintegration of the heat-sensitive recording material layer and to make the coloring agent in the heat-sensitive recording material layer water-soluble. [0010] As a coloring agent, organic acids such as phenolic compounds and aromatic carboxylic acids are generally used, but these become Na salts in Na0H solution and become solubilized in water, making them heat-sensitive. It is eluted from the recording material layer. On the other hand, basic dyes such as triallylmethane-based, phenylmethane-based, thiazine-based, and fluoran-based dyes do not react with the coloring agent in the form of Na salt to develop color. [0011] Here, in order to smoothly perform the action of NaOH with the waste heat-sensitive recording paper, NaOH is added in an amount of 1.0 to 10% by weight, preferably 1.0 to 5% by weight, based on the waste paper.
It is necessary to add within this range. Incidentally, if the amount of NaOH added exceeds 10% by weight, alkaline hydrolysis will occur.
The strength of the resulting recycled pulp decreases. On the other hand, 1.0
If the amount is less than % by weight, the coloring agent in the heat-sensitive recording material layer will not be sufficiently converted to Na salt. In addition, Na0 during disaggregation
When the temperature of the H aqueous solution exceeds 60°C, heat is applied to the heat-sensitive recording material layer before the coloring agent in the heat-sensitive recording material layer turns into Na salt, which develops color and adsorbs to the pulp fibers, resulting in the formation of recycled pulp. This is not preferred because the whiteness decreases. On the other hand, if the temperature is lower than 30°C, the binder contained in the heat-sensitive recording material layer and the resin in the protective layer become hard, and although the base paper layer is disintegrated, the disintegration of the heat-sensitive recording material layer and the protective layer becomes insufficient. . As a result, the coloring agent from the heat-sensitive recording material layer is not sufficiently converted into Na salt before proceeding to the next kneading step, so that the basic dye develops color in the kneading step. Moreover, the disintegration time is also long, which is an economical problem. Therefore, in the present invention, the liquid temperature of the alkaline aqueous solution during disintegration is specified to be 30 to 60°C. In the present invention, in order to efficiently disintegrate waste heat-sensitive recording paper with an alkaline aqueous solution, it is necessary to make the pulp concentration 10% by weight or more. That is, by specifying the pulp concentration to 10% by weight or more, the NaOH concentration in the solution inevitably increases, which not only promotes the disintegration of the base paper but also improves the mechanical bond between the pulp fibers and the heat-sensitive recording material layer. The friction also promotes disintegration of the heat-sensitive recording material layer. Incidentally, if it is 10% by weight or less, the NaOH concentration in the solution will also be low, and disintegration will be that much worse. As a result, in the post-disintegration process, a screen treatment is performed to remove foreign substances contained in the waste paper pulp, but at this time, undisintegrated pulp fibers are removed, reducing the yield of the resulting recycled pulp. It should be noted that if the pulp concentration exceeds 40% by weight, stirring and mixing will become difficult and disintegration will not be possible. Therefore, the pulp concentration at the time of disintegration is specified to be 10 to 40% by weight. [0013] Generally, in order to improve the recording sensitivity of heat-sensitive recording paints, it is necessary to micronize the material in each dispersion to a size of several microns or less during the paint preparation stage of the heat-sensitive recording material. In order to smoothly form particles into fine particles, auxiliary agents such as surfactants and protective colloids are often used during dispersion or wet grinding. Furthermore, since binders such as PVA and latex are used, a large amount of air is trapped in the disintegration (stirring) process of waste heat-sensitive recording paper containing these, resulting in the presence of large amounts of bubbles in the resulting suspension. become. These bubbles significantly reduce cleaning efficiency in processes such as dehydration concentration and washing, and cause heat-sensitive recording material to remain on the surface of the pulp fibers. In addition, the wastewater after dehydration and concentration is subjected to wastewater treatment such as coagulation flotation and coagulation sedimentation and is used as recovered water, but bubbles are generated during the treatment process, causing carryover and reducing wastewater treatment efficiency. Cause. In the present invention, in order to suppress these bubbles, an antifoaming agent is added in the defibration step. By adding an antifoaming agent, the heat-sensitive recording material layer can be efficiently separated from the pulp fibers, and recycled pulp with high whiteness and stable quality can be efficiently obtained. [0014] Specific antifoaming agents include polyglycol/fatty acid mixtures, phosphoric acid esters, silicone emulsion systems, nonionic fatty acid mixtures, polyglycol esters, alcohol systems, vegetable oil systems, fatty acid esters,
Examples include pine oil emulsion, sulfuric ester type, metal soap type, etc. The type thereof is not particularly limited, and may be appropriately selected depending on the type of used paper, liquid temperature, etc. The antifoaming agent may be added generally in an amount of about 0.0001 to 0.1% by weight based on the waste paper. Furthermore, if it is not sufficient to add the antifoaming agent in the disintegrating step, it is of course possible to add it immediately before entering the washing step or dehydration/concentration. In the present invention, the disintegrating machine used is not particularly limited, but a preferred disintegrating machine is preferably a high-density pulper having a helical rotor. When disintegrating waste heat-sensitive recording paper, if the waste paper contains pressure-sensitive adhesives, plastics, etc. (hereinafter simply referred to as foreign substances), it is natural that foreign substances will be mixed into the suspension after disintegration. Therefore, it is necessary to separate these foreign substances. A screening process is provided for the separation. In addition, when disintegrating this waste paper, if these foreign substances are subjected to excessive mechanical action by an agitator or the like, they may be broken into small pieces and slip out through the holes in the screen during the screening process, which may impair the separation effect. Not only that, but the recycled pulp also contains foreign matter. As a result, foreign matter may block the wire openings or contaminate press rolls or blankets during the papermaking process, causing paper breakage and significantly reducing productivity. In addition, it may cause spots on the paper surface, which may adversely affect the quality of the paper. [0016] Therefore, it is important to consider the degree of disintegration so that the foreign matter does not become finer than the holes in the screen. Usually, the screen step is installed at one or more locations after the disintegration step, after the mechanical stirring step, and after the foam flotation separation step. The installation location of the screen is not particularly limited, and may be appropriately selected depending on the amount, type, etc. of foreign matter. The suspension of waste heat-sensitive recording paper thus obtained is dehydrated and concentrated to a pulp concentration of 20% by weight or more. During this dehydration and concentration process, most of the heat-sensitive recording material, such as coloring agents and pigments, which have become Na salts and become water-soluble, are separated and removed from the pulp fibers. Although a known dehydrating and concentrating machine can be used in the dehydrating and concentrating step, a combination of an inclined screw thickener and a screw press is particularly preferably used in order to obtain the desired effects of the present invention. Next, it is necessary to disperse the granular heat-sensitive recording layer into fine particles by mechanically stirring strongly the waste paper pulp suspension whose pulp concentration has been adjusted to 20% by weight or more. Waste heat-sensitive recording paper with a protective layer that has properties such as water resistance, oil resistance, and plasticizer resistance is easily disintegrated in a normal disintegrator, but the heat-sensitive recording layer remains as granular particles. , mixed in the suspension. The thermosensitive recording material is present in these granules and cannot be easily removed. For this purpose, by adjusting the pulp concentration of the suspension to 20% by weight or more and performing mechanical stirring, it becomes possible to disperse the granular particles into fine particles. Incidentally, when the pulp concentration is less than 20% by weight, the dispersion efficiency is poor and granular particles remain in the suspension. A heat-sensitive recording material is contained in the granular particles. In addition, these granular particles cannot be removed by foam flotation separation in the subsequent process. If the pulp concentration exceeds 40% by weight, mechanical stirring and mixing becomes difficult, so the pulp concentration of the pulp suspension when performing mechanical stirring must be adjusted within the range of 20 to 40% by weight. . The method of mechanical stirring in the present invention refers to strong mechanical stirring accompanied by a compressive action, and for example, commonly used stirrers such as kneaders, twin-shaft mixers, and dispersers may be used as appropriate. There are no particular limitations. In addition, in the case of this mechanical stirring treatment, as in the disaggregation process, the heat-sensitive recording material still remains, so in order to suppress the color development of this heat-sensitive recording material, the temperature during the treatment was set to 60°C. It is preferable to maintain the following. After the mechanical high concentration stirring treatment, the pulp concentration is diluted to 2 to 5% by weight and further mechanical stirring is performed. This is because strong mechanical stirring is performed at a pulp concentration of 20% by weight or more in the previous step, so that the pulp fibers become entangled with each other and become ball-like. A portion of the heat-sensitive recording material is incorporated into the tangled hair bulb. This hair-ball-shaped pulp cannot be disentangled using the agitator installed in normal chests. Even if the next step of foam flotation separation is carried out in the state of this bulbous pulp suspension, the heat-sensitive recording material cannot be completely removed, and the whiteness of the obtained recycled pulp is reduced. For this purpose, mechanical stirring is carried out at a pulp concentration of 2 to 5% by weight to disentangle the pulp fibers and form them into single fibers. Equipment used for mechanical stirring at this time includes commonly used high-speed disintegrators, refiners, etc., and is not particularly limited. Furthermore, after adding a deinking agent to the waste paper pulp suspension that has undergone mechanical stirring treatment at a low concentration as described above,
The pulp concentration is adjusted to 0.3 to 1.5% by weight, air is blown into the pulp, and foam flotation separation is carried out to remove the heat-sensitive recording material still remaining in the pulp suspension together with the foam. The deinking agent used at this time can be a commonly used deinking agent for old newspapers, and in particular, a deinking agent consisting of fatty acid soap, fatty acid, and fat-based ethylene oxide/propylene oxide adducts can be used. is a preferred deinking agent because it has a strong tendency to adhere the heat-sensitive recording material to the surface of the bubbles and exhibits excellent effects in flotation and separation of the heat-sensitive recording material together with the bubbles in the bubble flotation process. The amount of deinking agent added is
It may be adjusted as appropriate depending on the foaming condition, and is usually added in an amount of 0.01 to 1.0% by weight based on the dry pulp. The deinking agent may be added at the time of foam flotation separation, but it is preferably added before the mechanical stirring step, especially in the mechanical stirring step when the pulp concentration is 20% by weight or more, so that the deinking agent is suspended in the pulp. This is a desirable embodiment because it is efficiently dispersed in the liquid. Furthermore, if the deinking agent is left to stand for one hour or more after mechanical stirring, the adsorption of the deinking agent to the heat-sensitive recording material becomes better, and the effect of separating the heat-sensitive recording material from the pulp is further improved. The foam flotation device used in the present invention is not particularly limited, and conventional floatators and the like can be used as appropriate. In addition, in the present invention, in order to further increase the whiteness of the recycled pulp obtained in this way, peroxide is added to the pulp suspension before entering the high concentration mechanical stirring step to The trace amount of heat-sensitive recording material remaining is oxidized and bleached. Examples of the peroxide include hydrogen peroxide, sodium peroxide, and sodium percarbonate, and are not particularly limited. The amount of peroxide added should be 0.2 to 5% by weight based on the pulp, and while measuring the whiteness of the pulp,
You can choose as appropriate. In addition, as a stabilizer for peroxide,
One or more selected from the group consisting of sodium silicate, chelating agents, sodium hydroxide, magnesium sulfate, etc., which are used in ordinary peroxide bleaching, are added in combination. [0023] If there are heavy foreign substances in the pulp, it is desirable to perform a cleaner treatment. On the other hand, if there are lightweight foreign substances, it is advisable to provide a lightweight foreign substance separation process such as Giroclean. Furthermore, it is preferable to provide a cleaning step to remove residual bleaching agent, decomposed products of the heat-sensitive recording material, residual deinking agent, and the like. As the cleaning method, displacement cleaning, dilution dehydration cleaning, press cleaning, etc. are used as appropriate. [0024] Furthermore, in order to increase the strength of the paper, it is possible to increase the pulp concentration to 3 to 4% by weight and beat the paper.
The degree of beating may be determined as appropriate depending on the quality target of the paper. The thus obtained white recycled pulp does not develop color during the papermaking process and has extremely few pinholes or speckled minute foreign matter, so it can be effectively used as a raw material for papermaking. [Examples] The present invention will be explained in more detail with reference to Examples below, but the present invention is of course not limited to these. In addition, % in an example shows "weight%." Example 1 [Disintegration process] Waste heat-sensitive recording paper having a protective layer on a pulper (manufactured by Aikawa Iron Works; high-concentration pulper), 1.5% NaOH was added to the waste paper, and an antifoaming agent ( Nopco 1407-K/manufactured by San Nopco Co., Ltd.) was added at 0.01% based on the dry solid content, and the pulp concentration was 1.
Warm water (55°C) was added so that the concentration was 5%, and the mixture was disintegrated for 30 minutes. [Screening process] The pulp suspension obtained above was diluted to a pulp concentration of 3.5%, and was screened using a screen with a slit width of 0.2 mm (Fine Screen/manufactured by Aikawa Iron Works). Processed. [Mechanical stirring step] Next, the accept was dehydrated and concentrated using a dehydration concentrator (tilt extractor, screw press, manufactured by Aikawa Tekko) so that the pulp concentration was 28%. To the dry solid content of this dehydrated and concentrated pulp, 2% hydrogen peroxide, 2% sodium silicate, and 0.3% deinking agent (DI-600 R/manufactured by Kao) were added, followed by strong mechanical stirring ( Disperser/manufactured by Aikawa Iron Works) treatment was performed. This mechanically agitated pulp was heated at 50°C.
After leaving for 100 minutes (ripening), the pulp was taken out and diluted to a pulp concentration of 4%, followed by dispersion using a high-speed disintegrator (Top Finer, manufactured by Aikawa Tekko). [Foam flotation separation process] The above-mentioned dispersion pulp suspension was further diluted to a pulp concentration of 1.0%, and stirred while introducing air. TATER (manufactured by Aikawa Iron Works) was used for flotation separation treatment. [Post-treatment step] Subsequently, the pulp suspension that has undergone the flotation separation process is passed through a cleaner for removing heavy foreign matter and a device for removing light foreign matter (Giroclean/manufactured by Aikawa Iron Works) for treatment. After that, it was dehydrated and concentrated. [Results] The recycled pulp thus obtained was
Finished into handmade sheets according to APPI STD T218, and after air-drying, the whiteness was measured using an Ellejo brightness meter (Ellejo 200
0). A handmade sheet with a tension of 60 g/m2 was prepared and measured in accordance with JIS Sp8113. The whiteness and tension obtained at this time were 83, respectively.
%, 3.7 Kg. Separately, paper was made by blending this recycled pulp and virgin pulp (50:50), but no color developed when the paper was heated in a dryer (heating). In addition,
The results obtained are shown in Table 1. Example 2 [Disintegration process] Used heat-sensitive recording paper with a protective layer on a pulper (high-density pulper/manufactured by Aikawa Tekko), and 5% Na0H added to the used paper, and an antifoaming agent (Nopco) DF-122 (manufactured by San Nopco) was added at 0.03% based on the dry solid content, and the pulp density was 20.
% of warm water (30°C) and disintegrated for 40 minutes. [Screen process] The above pulp suspension was diluted to a pulp concentration of 3.5% and treated using a screen with a slit width of 0.2 mm (Fine Screen/manufactured by Aikawa Iron Works). did. [Mechanical stirring step] Next, the accept was dehydrated and concentrated using a dehydration concentrator (tilt extractor, screw press, manufactured by Aikawa Iron Works) so that the pulp concentration was 30%. To the dry solid content of this dehydrated and concentrated pulp, 5% hydrogen peroxide, 3% sodium silicate, and 0.3% deinking agent (DI-610/manufactured by Kao) were added, followed by mechanical stirring (disperser). / Aikawa Iron Works) treatment was performed. After this mechanically agitated pulp was left at 50°C for 100 minutes, the pulp was taken out and the pulp density was 4.
% and dispersed the pulp using a high-speed disintegrator (Top Finer, manufactured by Aikawa Iron Works). [Foam flotation separation process] The above-mentioned dispersion pulp suspension was further diluted to a pulp concentration of 1.0%, and stirred while introducing air. TATER/manufactured by Aikawa Iron Works) for flotation separation treatment. [Post-treatment step] Subsequently, the pulp suspension that has undergone the flotation separation process is passed through a cleaner for removing heavy foreign matter and a device for removing light foreign matter (Giroclean/manufactured by Aikawa Iron Works) for treatment. After that, it was dehydrated and concentrated. [Results] The thus obtained recycled pulp was treated in the same manner as in Example 1, and the whiteness and tension of the handsheet were measured and were 84% and 3.6 kg, respectively. The results obtained are shown in Table 1. Note that paper was made from the same pulp in the same manner as in Example 1, but no color developed in the paper dryer. Example 3 [Disintegration process] A waste paper of heat-sensitive recording paper having a protective layer on a pulper (high concentration pulper/manufactured by Aikawa Tekko), 1.5% NaOH was added to the waste paper, and an antifoaming agent was added to the waste paper. (Form Clean M-48/manufactured by Hakuto Kagaku Co., Ltd.) was added at 0.03% based on the dry solid content, and warm water (45°C) was added so that the pulp concentration was 25%.
Disaggregated for minutes. [Rough Screening Step] The above pulp suspension was diluted to a pulp concentration of 3.5%, and then mixed using a screen with a slit width of 0.3 mm (Fine Screen/manufactured by Aikawa Iron Works). Processed. [Mechanical stirring step] Next, the accept was dehydrated and concentrated using a dehydration concentrator (tilt extractor, screw press, manufactured by Aikawa Tekko) so that the pulp concentration was 30%. Hydrogen peroxide 0.5% and sodium silicate 1% based on the dry solid content of this dehydrated and concentrated pulp.
, 0.3% of a deinking agent (DI-610/manufactured by Kao) were added, and mechanical stirring (disperser/manufactured by Aikawa Iron Works) was performed. This mechanically agitated pulp is
After standing at 0℃ for 100 minutes, the pulp was taken out, diluted to a pulp concentration of 4%, and placed in a high-speed disintegrator (
The pulp was dispersed using Aikawa Iron Works (Top Finer). [Foam flotation separation process] The above dispersion pulp suspension was further diluted to a pulp concentration of 0.7%, stirred while introducing air, and processed into a foam flotation device (vertical flotator/ (manufactured by Aikawa Iron Works) to perform flotation separation treatment. [Screen process] The above pulp suspension was treated using a screen (Fine Screen/manufactured by Aikawa Iron Works) with a slit width of 0.2 mm. [Post-treatment step] Subsequently, the pulp suspension that has undergone the flotation separation process is passed through a cleaner for removing heavy foreign matter and a device for removing light foreign matter (Giroclean/manufactured by Aikawa Iron Works) for treatment. After that, it was dehydrated and concentrated. [Results] The thus obtained recycled pulp was treated in the same manner as in Example 1, and the whiteness and tension of the handsheet were measured, and were found to be 81% and 3.8 Kg, respectively. The results obtained are shown in Table 1. Note that paper was made from the same pulp in the same manner as in Example 1, but no color developed in the paper dryer. Example 4 [Disintegration process] Used heat-sensitive recording paper having a protective layer on the pulper (high-density pulper/manufactured by Aikawa Tekko), 2% NaOH added to the used paper, and an antifoaming agent (Nopco) 1407-K/manufactured by San Nopco Co., Ltd.) was added at 0.01% based on the dry solid content, and the pulp concentration was 15%.
Warm water (55°C) was added so that the mixture was disintegrated for 30 minutes. [Rough screening process] The above pulp suspension was diluted to a pulp concentration of 3.5%, and then mixed using a screen with a slit width of 0.25 mm (Fine Screen/manufactured by Aikawa Iron Works). Processed. [Mechanical stirring step] Next, the accept was dehydrated and concentrated using a dehydration concentrator (tilt extractor, screw press, manufactured by Aikawa Tekko) so that the pulp concentration was 25%. To the dry solid content of this dehydrated and concentrated pulp, 1% hydrogen peroxide, 1% sodium silicate, and 0.3% deinking agent (DI-610/manufactured by Kao) were added, followed by mechanical stirring (disperser). / Aikawa Iron Works) treatment was performed. After this mechanically agitated pulp was left at 50°C for 50 minutes, the pulp was taken out, diluted to a pulp concentration of 4%, and dispersed using a high-speed disintegrator (Top Finer, manufactured by Aikawa Iron Works). did. [Screening process] The pulp suspension obtained above was further diluted to a pulp concentration of 1.0%, and then passed through a screen (with a slit width of 0.2 mm).
Fine Screen/manufactured by Aikawa Tekko). [Foam flotation separation process] The above-mentioned dispersion pulp suspension is stirred while introducing air, and the foam flotation separation device (
A vertical flotator (manufactured by Aikawa Iron Works) was used for flotation separation. [Post-treatment process] Subsequently, the pulp suspension that has undergone the flotation separation process is passed through a cleaner for removing heavy foreign matter and a device for removing light foreign matter (Giroclean/manufactured by Aikawa Iron Works) for treatment. After that, it was dehydrated and concentrated. [Results] The thus obtained regenerated pulp was treated in the same manner as in Example 1, and the whiteness and tension of the handsheet were measured and found to be 81% and 3.7 Kg, respectively. The results obtained are shown in Table 1. Note that paper was made from the same pulp in the same manner as in Example 1, but no color developed in the paper dryer. Example 5 [Disintegration process] A waste paper of heat-sensitive recording paper having a protective layer on a pulper (high concentration pulper/manufactured by Aikawa Tekko), 1.25% NaOH was added to the waste paper, and an antifoaming agent was added to the waste paper. (Nopco 1407-K/manufactured by San Nopco Co., Ltd.) was added at 0.07% based on the dry solid content, warm water (58° C.) was added so that the pulp concentration was 15%, and disintegration was performed for 30 minutes. [Rough screening process] The above pulp suspension was diluted to a pulp concentration of 3.5%, and then mixed using a screen (double separator/manufactured by Aikawa Iron Works) with a slit width of 0.3 mm. Processed. [Mechanical stirring step] Next, the accept was dehydrated and concentrated using a dehydration concentrator (tilt extractor, screw press, manufactured by Aikawa Tekko) so that the pulp concentration was 33%. Based on the dry solid content of this dehydrated and concentrated pulp, 1% hydrogen peroxide, 2.5% sodium silicate,
0.6% of a deinking agent (DI-600R/manufactured by Kao) was added to each, and mechanical stirring (disperser/manufactured by Aikawa Iron Works) was performed. This mechanically agitated pulp is
After being left at 0°C for 120 minutes, the pulp was taken out, diluted to a pulp concentration of 4%, and placed in a high-speed disintegrator (
The pulp was dispersed using Top Finer (manufactured by Aikawa Tekko). [Foam flotation separation process] The above dispersion pulp suspension was further diluted to a pulp concentration of 1%, stirred while introducing air, and foam flotation device (vertical flotator/Aikawa Tekko Co., Ltd.) was used. The flotation separation process was carried out using the following methods: [Screen Step] The above pulp suspension was diluted to a concentration of 1% and subjected to a selective treatment using a screen with a slit width of 0.2 mm (Fine Screen/manufactured by Aikawa Tekko). [Post-treatment process] Subsequently, the pulp suspension that has undergone the flotation separation process is passed through a cleaner for removing heavy foreign matter and a device for removing light foreign matter (Giroclean/manufactured by Aikawa Iron Works) for treatment. After that, it was dehydrated and concentrated. [Results] The thus obtained recycled pulp was treated in the same manner as in Example 1, and the whiteness and tension of the handsheet were measured, and they were 82% and 3.8 Kg, respectively. The results obtained are shown in Table 1. Note that paper was made from the same pulp in the same manner as in Example 1, but no color developed in the paper dryer. Comparative Example 1 A recycled pulp was prepared and treated in the same manner as in Example 1, except that the addition of NaOH and antifoaming agent used in the disintegration step was stopped. The tension of the handmade sheet of recycled pulp obtained at this time was 3.8 kg, but the El Rejo whiteness was 60%, which was quite poor compared to Example 1. )
The paper made with this mixture developed a little color in the dryer. The results obtained are shown in Table 1. Comparative Example 2 The preparation and treatment were carried out in the same manner as in Example 1, except that the addition of the antifoaming agent used in the defibration step was stopped and the temperature of the hot water was changed to 70°C. Obtained pulp. The tension of the handmade sheet of recycled pulp obtained at this time was 3
.. 7 kg, but the El Rejo whiteness was 70%, which was poor compared to Example 1.
The paper made with a blend of 0:50) developed a little color in the dryer. The results obtained are shown in Table 1. Comparative Example 3 The preparation and treatment were carried out in the same manner as in Example 1 except that the addition of the antifoaming agent used in the defibration step was stopped and the pulp concentration was changed to 6%. Obtained pulp. The tension of the handmade sheet of recycled pulp obtained at this time was 3.9 kg, but the El Rejo whiteness was 73%, which was poor compared to Example 1. The paper made with the blend developed a little color in the dryer. The results obtained are shown in Table 1. Comparative Example 4 The preparation and treatment were carried out in the same manner as in Example 1 except that the addition of NaOH was changed to 1.2%.
Regenerated pulp was obtained. The Elleho whiteness of the recycled pulp obtained at this time was 83%, which is the same as in Example 1, but the tension of the handsheet was reduced to 3.0 kg. The results obtained are shown in Table 1. Comparative Example 5 In Example 1, the amount of NaOH used in the disintegration step was 0.5%, and the pulp concentration in the mechanical stirring step was 10%.
Regenerated pulp was obtained by preparing and treating in the same manner as in Example 1, except that the respective percentages were changed. The tension of the handmade sheet of recycled pulp obtained at this time was 3.7 kg, but the El Rejo whiteness was 62%, which was considerably worse than that of Example 1, and the recycled pulp and virgin pulp (50:5
Paper made with 0) produced granular colored spots when exposed to a dryer. The results obtained are shown in Table 1. [Table 1] [Effects of the Invention] As is clear from the examples, recycled pulp obtained from waste heat-sensitive recording paper provided with a protective layer can maintain high whiteness; Moreover, even when the paper sheet obtained from the recycled pulp of the waste paper was heated, no color development or granular colored spots were observed.

Claims

【特許請求の範囲】 【請求項1】感熱記録紙の古紙をNaOH水溶液中で離
解して離解パルプとした後、脱墨剤及び過酸化物を添加
し、次いで該離解パルプを高濃度機械的攪拌処理する方
法において、下記条件(a) 〜(d) を満足するよ
うに処理することを特徴とする感熱記録紙古紙の再生パ
ルプ化法。 (a) ; NaOH水溶液が消泡剤を含む(b) ;
 NaOHの濃度が古紙パルプに対し、1〜10重量% (c) ; 離解時のNaOH水溶液の温度が30〜6
0℃(d) ; 離解時の古紙パルプの濃度が10重量
%以上
      【請求項2】感熱記録紙が保護層を有
する請求項1記載の再生パルプ化法。
[Claims] Claim 1: A method in which waste heat-sensitive recording paper is disintegrated into a disintegrated pulp in an aqueous NaOH solution, a deinking agent and a peroxide are added, and then the disintegrated pulp is subjected to high-concentration mechanical stirring treatment, A method for producing recycled pulp from waste heat-sensitive recording paper, which is characterized in that it is processed so as to satisfy the following conditions (a) to (d). (a); The NaOH aqueous solution contains an antifoaming agent (b);
The concentration of NaOH is 1 to 10% by weight based on the waste paper pulp (c); The temperature of the NaOH aqueous solution during disintegration is 30 to 6% by weight
0℃(d); The concentration of waste paper pulp at the time of disintegration is 10% by weight or more
2. The recycled pulping method according to claim 1, wherein the thermosensitive recording paper has a protective layer.
JP2405620A 1990-12-25 1990-12-25 Method for recycling and pulping waste heat-sensitive recording paper Pending JPH04222284A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2405620A JPH04222284A (en) 1990-12-25 1990-12-25 Method for recycling and pulping waste heat-sensitive recording paper

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2405620A JPH04222284A (en) 1990-12-25 1990-12-25 Method for recycling and pulping waste heat-sensitive recording paper

Publications (1)

Publication Number Publication Date
JPH04222284A true JPH04222284A (en) 1992-08-12

Family

ID=18515231

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2405620A Pending JPH04222284A (en) 1990-12-25 1990-12-25 Method for recycling and pulping waste heat-sensitive recording paper

Country Status (1)

Country Link
JP (1) JPH04222284A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5755926A (en) * 1992-02-24 1998-05-26 Kimberly-Clark Worldwide, Inc. Integrated pulping process of waste paper yielding tissue-grade paper fibers
JP2002069876A (en) * 2000-08-22 2002-03-08 Nippon Paper Industries Co Ltd Method for deinking waste paper
KR100553581B1 (en) * 2002-03-05 2006-02-22 한재호 Method for recycling air-filter paper of automobile
CN103835174A (en) * 2012-11-27 2014-06-04 广州瑞辰盛达生物技术有限公司 Wet-strength waste paper pulping method
JP2015078469A (en) * 2013-10-18 2015-04-23 北越紀州製紙株式会社 Regeneration method of waste paper containing waste laminate paper
JP2016507673A (en) * 2013-07-16 2016-03-10 チュエン オウ,カム Waterproof recycled paper and production method thereof
JP2017125266A (en) * 2016-01-12 2017-07-20 王子ホールディングス株式会社 Manufacturing method and manufacturing system of deinked waste paper pulp

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5755926A (en) * 1992-02-24 1998-05-26 Kimberly-Clark Worldwide, Inc. Integrated pulping process of waste paper yielding tissue-grade paper fibers
JP2002069876A (en) * 2000-08-22 2002-03-08 Nippon Paper Industries Co Ltd Method for deinking waste paper
KR100553581B1 (en) * 2002-03-05 2006-02-22 한재호 Method for recycling air-filter paper of automobile
CN103835174A (en) * 2012-11-27 2014-06-04 广州瑞辰盛达生物技术有限公司 Wet-strength waste paper pulping method
JP2016507673A (en) * 2013-07-16 2016-03-10 チュエン オウ,カム Waterproof recycled paper and production method thereof
JP2015078469A (en) * 2013-10-18 2015-04-23 北越紀州製紙株式会社 Regeneration method of waste paper containing waste laminate paper
JP2017125266A (en) * 2016-01-12 2017-07-20 王子ホールディングス株式会社 Manufacturing method and manufacturing system of deinked waste paper pulp

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